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Center
for Embedded Networked Sensing (CENS) Using Cyclops-7 Fluorometer
in Monitoring of Algal Blooms
About CENS:
CENS, a NSF Science & Technology Center, is developing Embedded
Networked Sensing Systems and applying this revolutionary technology
to critical scientific and social applications. Like the Internet,
these large-scale, distributed, systems, composed of smart sensors
and actuators embedded in the physical world, will eventually
infuse the entire world, but at a physical level instead of virtual.
Project
Overview:
A specific area in which CENS technology is being applied is the
monitoring of harmful algal blooms (HABs). A variety of naturally-occurring
and introduced microorganisms adversely impact marine ecosystems
and uses of marine resources. They can affect human health, fisheries
and even tourism. However, conditions under which HABs develop
are not well understood, and methods for detecting microorganisms
are too slow and complex for timely intervention. With the development
of technology, sensor networks provide a method to monitor the
microorganisms in real time and solve the problem. The goal of
this project is to deploy large numbers of sensors and robots
operating in a semi-autonomous but coordinated fashion in the
marine environment (Figure 1). The system should be able to follow,
identify and investigate the behavior of microorganisms in situ
and in real time.

Figure
1: (center) Schematic of autonomous, coordinated network of mobile
sensors. (upper left) Testing of wireless communication between
nodes in tank testbed. (upper right) Autonomous, mobile node equipped
with computer-controlled mobility, communications, sampling system,
and Turner Designs Cyclops-7 fluorometer. (center bottom) Submersible
node to be used as a data mule or for obtaining vertical profiles.
Approach:
We are studying the dynamics of blooms of the alga Aureococcus
anophagefferens in the waters off Long Island, NY. Existing monitoring
efforts are time-consuming and involve manual sampling and analysis.
We are constructing a network of sensors and samplers, consisting
of both stationary and mobile “nodes,” to allow for spatially-
and temporally-rigorous monitoring and adaptive sampling. For
example, changes in temperature or chlorophyll fluorescence can
serve as triggers for sampling (Figure 2).

Figure
2: Concentration of Aureococcus anophagefferens (BT) and temperature
with depth in a column testbed. Note the decrease in BT concentration
(black profile) around the point of the thermocline (gray profile).
The stationary
nodes consist of temperature and salinity sensors, Turner Designs
Cyclops-7 chlorophyll a fluorometers, and associated processors
and communications equipment (Figure 3).
Figure
3: Schematic of stationary node components.
These environmental
sensors measure at a high frequency and signal bloom events (e.g.
elevated chlorophyll levels). We are then be able to deploy the
more complex mobile node (Figure 4) to make more sophisticated
measurements and retrieve relevant samples.

Figure
4: Mobile node equipped with wireless communication, computer-controlled
mobility and navigation, sampling system, and Turner Designs Cyclops-7
fluorometer.
The Turner
Designs Cyclops-7 chlorophyll fluorometer is an integral part
of the network of sensors. As a proxy for photosynthetic biomass,
chlorophyll measurement is one of the most biologically-significant
parameters to measure in marine systems. Previous blooms of A.
anophagefferens have shown chlorophyll a levels between 5 and
50 ìg/L, although higher values are possible. We chose
to use the Turner Designs Cyclops-7 fluorometer because of its
flexible sensitivity ranges, low power requirements and small
size.
Further
information:
For additional information on this project, please contact:
Beth Stauffer
Research Lab Technician
Dept of Biological Sciences
University of Southern California
Phone: (213) 821-2123
E-mail: stauffer@usc.edu
URL: www.usc.edu
Or:
Carl Oberg
Engineering Technician
University of Southern California
Computer Science
SAL 206
941 West 37th Place
Los Angeles, California 90089-0781
Phone: (213) 740-0541
E-mail: oberg@usc.edu
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Bacterial
Source Tracking in Puerto Rico with Turner Fluorometers
This January
we brought two Turner 10-AU field fluorometers to southwestern
Puerto Rico to see how well they worked for bacterial source tracking.
Bacterial source tracking tries to identify sources of fecal contamination
using a variety of phenotypic, genotypic, and chemical methods.
We wanted to use the fluorometers to detect optical brighteners-
the colorless, fluorescent dyes in laundry detergents that make
clothing "whiter than white." Because laundry detergent
residues are often associated with human sewage, the combination
of high fecal bacterial counts and the presence of optical brighteners
in surface waters suggests that human fecal contamination is present
(Table 1)
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Bacterial
Count
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Optical
Brightener
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Likely
Result |
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High
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High
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Malfunctioning
septic system or leaking sewer pipe |
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High
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Low
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Non-human
warm-blooded animals |
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Low
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High
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Gray
water in storm water system |
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Low
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Low
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No
evidence of fecal contamination at the time |
Table
1. Four possible outcomes when fluorometry for optical brighteners
is combined with counts of fecal indicator bacteria.
To detect
human fecal contamination, we combined field fluorometry with
targeted sampling for Escherichia coli, a bacterium widely used
as an indicator of fecal contamination. Targeted sampling is much
like the children's game of "hot and cold," and requires
sampling and resampling for fecal bacteria until a persistent
source of the bacteria is identified (Kuntz et al., 2003). We
used the IDEXX Colilert system to identify high numbers of E.
coli.

This was our
first study to combine fluorometry and targeted sampling beyond
our preliminary work on the Georgia coast (Gates et al., 2004).
Overall, the system seemed to work well. For example, we observed
high counts of E. coli and high fluorometric signals in the Yaguez
River, which flows through the city of Mayagüez. We are confirming
these data with PCR analysis for the presence of human virulence
factor. The clear waters in Puerto Rico were an ideal testing
ground for fluorometry because organic matter didn't interfere
with the fluorometric signal. We are continuing to develop the
combination of fluorometry and targeted sampling for Georgia waters,
where high amounts of organic matter in the water do interfere
with the fluorometric signal. However, for the moment, the data
are encouraging for places like Puerto Rico.

References:
Kuntz, R. L., P. G. Hartel, D. G. Godfrey, J. L. McDonald, K.
W. Gates, and W. I. Segars. 2003. Targeted sampling protocol with
Enterococcus faecalis for bacterial source tracking. J. Environ.
Qual. 32:2311-2318.
Gates, P.,
P. Hartel, K. Payne, J. McDonald, K. Austin, K. Rodgers, J. Fisher,
S.N.J. Hemmings, and L. Gentit. 2004. Combining targeted sampling
and bacterial source tracking to determine sources of fecal contamination
to the south beach of Sea Island during calm and stormy conditions.
Sea Island Company. 12 p.
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Cornell
Researchers Use Aquafluor Fluorometer To Measure Ammonia Excretion
By Tropical Fish
Pete McIntyre,
a researcher at Cornell University, selected a Turner Designs
Aquafluor fluorometer to measure ammonia in water as part of a
research project investigating the impacts tropical freshwater
fish have on nutrient cycling in their ecosystem.
Application
Introduction
Tropical fishes are renowned for their species diversity, interesting
behaviors, and beautiful coloration. Most people associate tropical
fish primarily with coral reefs, but species inhabiting tropical
freshwaters account for 20-25% of the world’s total fish species
diversity! Despite their impressive diversity, scientists are
only beginning to understand the ways in which these fishes affect
the functioning of tropical freshwater ecosystems.
There is a
growing list of threats to tropical freshwater fish diversity,
including overfishing, habitat degradation, introduced species,
and river impoundments. At the same time, the number of humans
dependent upon the rich fisheries of tropical rivers and lakes
grows every year. These shifts raise critical question about whether
every species plays a unique role in its ecosystem, or instead
most species are equivalent in their functional roles.
Application
Objectives
Pete McIntyre’s research addresses the functional contributions
of tropical fishes to their ecosystems through nutrient recycling.
Biologists have long recognized that animals are not very efficient
at retaining the nutrients in their food, and some of these nutrients
are returned to the environment in forms that are readily available
to fuel new productivity of plants. In the case of fishes, most
species excrete a substantial proportion of their dietary nitrogen
as ammonia (NH3) that is released continuously across the gills.
In ecosystems where nitrogen availability limits the productivity
of algae, the recycling of dietary nitrogen by fishes could be
a critical part of the nutrient cycle.
Application
Results
In collaboration with Alex Flecker (Cornell University) and Mike
Vanni (Miami University, Ohio), he studied the excretion of NH3
and dissolved phosphorus by fishes in a piedmont river in Venezuela.
This site is home to around 80 species of fishes, including a
variety of catfishes and tetras. They are investigating the determinants
of nitrogen and phosphorus recycling rates, including species
identity, body size, body composition, and diet. Their work has
revealed great variation among species, much of which is explained
by body size and composition (see Vanni et al. 2002. Ecology Letters
5: 285-293).
Their field
site is not linked into a power grid, so they have always had
to rely on portable field equipment that requires little power.
For the last two years, they have been using a Turner Designs
Aquafluor handheld fluorometer to obtain high-resolution NH3-N
data in the field using only battery power. Using the OPA detection
method developed by Holmes et al (1999), they have been very pleased
with the instrument’s precision and linearity up to ~90 µg
N/L when checked against a Turner 10-AU or autoanalyzer. Others
in their research team have been equally pleased with the accuracy
of low-level measurements (1-8 µg NH3-N/L) taken with the
Aquafluor. The Aquafluor’s portability for air-travel and battery
power for fieldwork made it a critical part of his research in
South America and Africa.
They have
now expanded their Venezuelan project to measure NH4 recycling
by almost 50 species of fishes, and the results indicate that
fishes play a critical role in quickly regenerating nutrients
in this N-limited ecosystem. This information is now being combined
with surveys of the fish community to determine the importance
of individual species in the ecosystem.

We
collect fish from riffles by stirring the rocks under which they
hide in Rio Las Marias, Venezuela. By exhaustively collecting
from many such quadrats, we can estimate the typical density of
benthic fishes in the river.

Dozens
of species of fish live in small riffles like this one. Some species
feed on algae growing on the rocks, others eat the riparian vegetation,
and many hunt for insects and crustaceans.

We
catch fish from the river and incubate them in bags of water to
measure their nutrient excretion.
For further
information, please visit:
http://www.eeb.cornell.edu/flecker/flecker.html
http://www.eeb.cornell.edu/

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Dye
Selection for Groundwater Studies & The Use of Multiple Dyes
Question:
What is the best
type of fluorescent tracer dye to use for groundwater studies, and
can more than one dye be used simultaneously?
Answer:
Rhodamine and
Uranine (Fluorescein) are popular fluorescent dyes that have been
used for groundwater tracing for over 20 years. The paper at the
link below, discusses the properties of the dye and the composition
of the ground media to help select the best dye to use to avoid
any sorption effects that can retard the dye movement. Dye
Properties & Ground Media Paper
There can be
advantages in using Rhodamine and Uranine dye at the same time.
For example, each dye can be deposited at a different location (well
site) and then a fluorometer is used to monitor at a sampling well
to determine whether either or both dyes is present. The fluorometer
has to be set up with both the Rhodamine and Fluorescein optics,
to detect the respective dye. You should expect about 5% overlap
on the detection. As an example, if you measured a sample that only
contains a 100 ppb concentration of Rhodamine dye on the fluorometer
that is configured for Fluorescein, then you should expect to get
a reading of approxomately 5 ppb. The same is true for a Uranine
sample read on the fluorometer that is configured for Rhodamine.
As long as one
dye is not over 10 times the concentration of the other, the reading
of a sample containing both dyes can be mathematically corrected
to derive at the actual concentration, if quantitative accuracy
is required. The majority of groundwater tracer tests, are only
interested in determining the time it took for a given dye to be
detected in the sampling well and are not concerned with the quantitative
accuracy.
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Technically
Speaking, It All Adds Up…….
is a series
of articles for people who want to obtain the best possible results
from their fluorometer. This month's article will provide information
on getting to quantitative results, (absolute values) when making
in vivo chlorophyll measurements.
When you consider
in vivo chlorophyll measurements, you need to remember that
this is a relative measure of algal biomass. If you require quantitative
data of in vivo Chlor a, there are several factors that can
create a challenge. These factors include variations in the species,
physiological effects, ambient light impacts on fluorescence, and
the presence of interfering compounds such as dissolved organic
matter. (see Guide
to In Vivo Chlorophyll Measurement to learn more):
These factors
mean that ideally, each sensor would be calibrated before being
deployed, (pre-calibration) using the actual water to be measured.,
Normally, it is not practical for the user to perform an initial
primary calibration with natural water samples containing Chlor
a concentrations that have been precisely determined. Routinely,
a "post calibration" method is performed, where the user
performs extractions of the chlorophyll a from water samples collected
during the field work. The extracted samples are performed in the
Lab as described in the EPA methods, see link below. The extracted
chlorophyll a results are then correlated with the in vivo
value for a given water sample.
Therefore, before heading into the field to perform in vivo
Chlor a sampling with a fluorometer, the user only needs to perform
a calibration with a secondary standard, such as Turner Designs
solid standards or a fluorescent dye solution. The same secondary
standard can later be used to check the instrument performance,
and can be used to check multiple instruments at varying times.
Using the secondary standard with multiple sensors would ensure
consistent and repeatable readings across the instruments. If a
digital instrument is being used, a relative value can be assigned
to the solid standard during the calibration, such as 100, and this
can be checked at different times to check for biofouling, or instrument
drift. When using analog sensors, the user would simply note the
signal level with the secondary standard installed.
The blank level
should also be noted before deployment. The best blank solution
is filtered sample water. This will remove all algal cells, but
dissolved material that can cause some interference to the fluorescent
reading will stay in solution and thus be corrected for by noting
the blank level.
With the performance
check and blanking complete, the sensor can be deployed. At the
time of deployment and at regular intervals during deployment, water
samples should be collected. At the time of collection, the in
vivo fluorescence of the same water sample needs to be recorded.
NOTE:
If you are using a submersible fluorometer, and plan to capture
and read samples in a small container, then care needs to be taken
to ensure the container itself is not interfering with the reading
by a) placing the sensor too close to the bottom or sides or b)
the container itself is not fluorescing or reflecting light. Refer
to the instrument's User Manual for details.
Once the in
vivo reading of the sample has been recorded, some of the water
needs to be processed for extracted chlorophyll analysis. This is
most commonly done through fluorometry, spectrophotometry, or HPLC
analysis. Refer to EPA methods 445,446 and 447 respectively. After
the quantitative chlorophyll a concentration has been determined
through extracted analysis, the in vivo and extracted values
of a given water sample are used to develop a correlation, see graph
below.
This is done
for all water samples collected in a given environment (different
correlations should be developed for different bodies of water),
and the average correlation for a given environment is used to correct
all of the in vivo data for that region. This is how in vivo
fluorometer data is best handled for good quantitative estimates
of the Chlor a.
EPA link = http://www.epa.gov/nerlcwww/ordmeth.htm

Figure 1: Once the graph has been generated,
it can be used to obtain quantitative results for all the in vivo
fluorometer data.
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Turner
Designs 10-AU Fluorometer Rental Program
Do
you have an upcoming project that requires the use of the 10-AU
Field Fluorometer but don't have a long-term need and/or the budget
for an instrument? Turner Designs recognizes that some of our customers
meet this criteria, which is why we stock a pool of rental 10-AU
Field Fluorometers to help meet the short-term project requirements
of some of our customers.
The 10-AU Field
Fluorometer is our most stable, rugged, versatile, and sensitive
unit, and our rental units include all of the possible options that
our customers might need. These options include:
- One optical
kit specific to your application (i.e. rhodamine WT, fluorescein,
chlorophyll, etc.)
- A flow cell
for continuous measurements, and a test tube adapter for discrete
measurements (customer can indicate which one to have installed)
- Internal
data logging capabilities (>64,000 data points)
- Temperature
compensation capabilities
- Cables to
allow for powering with a 12VDC battery or 115-230VAC
- Spreadsheet
interface software
- Weather-tight
case for rugged field use
- Shipping
case for transporting unit
Minimum rental
period is two weeks, and standard pricing is available for two week
and monthly increments. For more details on our 10-AU Rental Program,
or to set up a rental, please contact Patrick
Sanders at (877)316-8049 ext 117.
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